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96Vol.9No.620156ChineseJournalofEnvironmentalEngineeringJun.2015Fered-Fenton122323*2312311.1000832.1000123.100012Ti、TiRuO2Fered-Fenton。H2O2、Fe2+、pH。H2O275.0mmol/LFe2+7.5mmol/LpH3.05.1mA/cm2120minTOC198.2mg/L99.6mg/L49.7%BOD5/COD0.110.31。EEMFered-Fenton、66.7%。Fered-FentonX703A1673-9108201506-2653-07TreatmentofreverseosmosisconcentrateofpetrochemicalwastewaterbyFered-FentonprocessFanDongqi12WeiJian23SongYonghui23ZengPing23CuiXiaoyu123XuDongyao11.SchoolofChemicalandEnvironmentalEngineeringChinaUniversityofMiningandTechnologyBeijing100083China2.ScientificandTechnologicalInnovationBaseofUrbanWaterEnvironmentalResearchChineseResearchAcademyofEnvironmentalSciencesBeijing100012China3.StateKeyLaboratoryofEnvironmentalCriteriaandRiskAssessmentChineseResearchAcademyofEnvironmentalSciencesBeijing100012ChinaAbstractAFered-FentonsystemusingTisheetascathodeandRuO2/Tiasanodewasestablishedfortreatingreverseosmosisconcentrateofpetrochemicalwastewater.TheeffectsofH2O2andFe2+concentrationin-itialpHandappliedcurrentontreatmentefficiencywereinvestigated.Furthermorethevariationsofbiodegrad-abilityandcharacteristicpollutantswerealsoanalyzed.TheresultsshowedthattheoptimumreactionconditionswereH2O2dosageof75.0mmol/LFe2+dosageof7.5mmol/LinitialpHvalueof3.0andcurrentintensityof5.1mA/cm2.Afterreactionof120mintheTOCconcentrationdecreasedfrom198.2mg/Lto99.6mg/Lcorrespondingtoorganicsmineralizationefficiencyof49.7%.TheorganicpollutantsconcentrationsignificantlydecreasedandthebiodegradabilitywasobviouslyimprovedwiththeBOD5/CODratioincreasingfrom0.11to0.31.Theexcitation-emissionmatrixEEMspectrumanalysisdemonstratedthatthetotalremovalefficiencyoffluorescenceorganicsincludingprotein-likeandfulvicacidssubstancesreached66.7%byFered-Fentontech-niquewhichwasinfavorofimprovementofbiodegradabilityandfurtherbiologicaltreatment.KeywordsreverseosmosisconcentrateROCFered-Fentonbiodegradabilityexcitation-emissionma-trixEEM2012ZX07202-0022012ZX07202-005211071032014-12-232015-02-051988—。E-mailfandongqi1120@126.com*E-mailsongyh@craes.org.cn·OH。Fenton、、1。Fenton、、2。Fenton、9。Fered-FentonFenton。Fered-FentonFentonH2O2/Fe2+3H2O2Fe2+·OH1。Fered-Fen-tonFentonFe3+Fe2+2FentonFe2+4。Fered-Fenton5Fe2++H2O2→Fe3++·OH+OH-1Fe3++H2O2→Fe2++·HO2+H+2·OH+H2O2→·HO2+H2O3·OH+Fe2+→Fe3++OH-4Fe3++·HO2→Fe2++O2H+5Fe2++·HO2+H+→Fe3+62·HO2→H2O2+O27。、、。、Fenton、、、67。Fered-FentonH2O2、Fe2+、pH。11.1“-”COD、BOD5、TOCNH+4-N580、62、19886mg/LpH6.5。1.21、、。RuO2/TiTi10.0cm×6.0cm。400mL2.5cm6.0cm×6.0cm。80.0mmol/LNa2SO41.0mol/LH2SO4pHFeSO4·7H2OH2O21.0mol/LNaOHpH10.030min0.45μm。H2O230%w/w、FeSO4·7H2O、Na2SO4、H2SO4、NaOH。1Fered-FentonFig.1SchematicdiagramofFered-Fentonexperimentalsetup1.3CODCR3200CODWTWBOD5NH+4-NUnicoUV-2102cUnicoTOCTOC-LCPHCN200pHDZS-706。F-7000。、10。Ex=200~450nmEm=260~550nm5nmPMT700V2400nm/min。Milli-Q。45626Fered-Fenton1.4、FRIEEM89。5IIIEx/Em=200~250nm/260~330nmEx/Em=200~250nm/330~380nmIIIIVEx/Em=200~250nm/>380nmEx/Em=250~450nm/260~380nmVEx/Em=250~450nm/>380nm。Origin9.0ΦiΦin10Pin。22.1H2O2TOCFe2+7.5mmol/LpH3.05.1mA/cm2H2O2TOC。2。H2O2TOCH2O275.0mmol/LTOCH2O2100.0mmol/L125.0mmol/LTOC51.0%44.5%。H2O2·OHTOC。H2O22H2O2TOCFig.2EffectofH2O2concentrationonTOCremovalefficienciesH2O2Fe2+Fe3+H2O211H2O2·OH·HO12-1423H2O2·OH。H2O275.0mmol/L。2.2Fe2+TOCH2O275.0mmol/LpH3.05.1mA/cm2Fe2+TOC3。3Fe2+2.5mmol/L7.5mmol/LTOC35.5%49.7%。Fe2+10.0mmol/LTOC46.2%。Fered-FentonFe2+H2O2·OHFe2+·OH。Fe2+Fe2+·OH1516·OH。Fe2+17H2O2·OOH818。Fe3++H2O2→Fe2++·OOH+H+83Fe2+TOCFig.3EffectofFe2+concentrationonTOCremovalefficiencies2.3pHTOCH2O275.0mmol/LFe2+7.5mmol/L5.1mA/cm2pHTOC4。Fered-FentonpH3.0TOC49.7%。pH3.055629pHpH014.0·OH2.8V1.9V19·OH。pHH2O220Fe2+FeOH3Fe2O3·OH。pH3.0H+H2O2H3O2+H2O2H2O2Fe2+21。4pHTOCFig.4EffectofinitialpHvalueonTOCremovalefficiencies2.4TOCH2O275.0mmol/LFe2+7.5mmol/LpH3.0TOC5。52.6mA/cm212.8mA/cm2TOC5.1mA/cm2TOC49.7%。12.8mA/cm2TOC41.8%。Fe3+Fe2+Fenton·OHTOC22。H2O2923·OH。H2O2+2H++2e-→2H2O95.1mA/cm2。2.524。BOD5/CODB/C5TOCFig.5EffectofelectriccurrentintensityonTOCremovalefficiencies<0.32526。COD580mg/L、BOD562mg/LCOD278mg/L、BOD587mg/LB/C0.110.31。Fered-FentonTOC198.2mg/L99.6mg/L49.7%。Fered-Fenton。2.6Fered-FentonH2O275.0mmol/LFe2+7.5mmol/LpH3.05.1mA/cm26。27IIIIII、、IVV。EEM2A、C。AⅢExEm250430nmCVExEm335390nm。120min。65626Fered-Fenton6Fig.6EEMspectraofwastewateratdifferentreactiontimesFRIEEM5Φin1。1ΦIn、ΦⅡn、ΦⅢn、ΦⅣn、ΦⅤn56.2%、69.4%、67.8%、63.0%、62.3%。Fered-Fenton5。76EEMPin。ⅢPinPin。ⅢⅠ、ⅡⅠ、ⅡⅢ。ⅢPin。Ⅰ、Ⅱ、ⅣVPin。。1Table1Normalizedexcitation-emissionareavolumesofallfluorescenceregionsatdifferenttimesminΦInΦⅡnΦⅢnΦⅣnΦⅤnΦTn079828.7534734.0463248.8243671.963388.01384871.41539933.8262462.4338115.1111940.150844.6803296.03036057.9193531.8298526.799632.447156.0674904.96037872.7154642.1187867.589949.930488.1500820.39037475.3154730.1150483.488175.724992.9455857.412034979.6163604.4149149.290140.123917.2461790.5756297EEMPinFig.7PindistributionsinEEMspectraatdifferenttimes3Fered-FentonH2O275.0mmol/L、Fe2+7.5mmol/L、pH3.05.1mA/cm2120minTOC49.7%COD52.1%66.7%B/C0.110.31。Fered-Fen-ton。1ChoiH.Al-AbedS.R.DionysiouD.D.etal.TiO2-basedadvancedoxidationnanotechnologiesforwaterpurifi-cat
本文标题:FeredFenton法处理石化废水反渗透浓水
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